Coffee mucilage impact on young coffee seedlings and soil microorganisms
A greenhouse pot experiment was carried out to assess the effects of fermented coffee mucilage applied as mulch together with maize leaves on the growth of young coffee plants of two different varieties and on soil microbial biomass indices. The coffee variety Catuai required 32% more water per g pl...
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Veröffentlicht in: | Journal of plant nutrition and soil science 2019-10, Vol.182 (5), p.782-790 |
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description | A greenhouse pot experiment was carried out to assess the effects of fermented coffee mucilage applied as mulch together with maize leaves on the growth of young coffee plants of two different varieties and on soil microbial biomass indices. The coffee variety Catuai required 32% more water per g plant biomass than the variety Yellow Caturra, but had a 49% lower leaf area, 34% less shoot and 46% less root biomass. Maize and mucilage amendments did not affect leaf area, shoot and root yield, or the N concentration in shoot and root dry matter. The amendments always reduced the water use efficiency values, but this reduction was only significant in the maize+mucilage‐14 (= 14 g mucilage pot−1) treatment. Soil pH significantly increased from 4.30 in the control to 4.63 in the maize+mucilage‐14 treatment. Microbial biomass C increased by 18.5 µg g−1 soil, microbial biomass N by 3.1 µg g−1 soil, and ergosterol by 0.21 µg g−1 soil per g mucilage added pot−1. The presence of mucilage significantly reduced the microbial biomass‐C/N ratio from a mean of 13.4 in the control and maize treatments to 9.3, without addition rate and coffee variety effects. The application of non‐composted mucilage is recommended in areas where drought leads to economic losses and in coffee plantations on low fertility soils like Oxisols, where Al toxicity is a major constraint. |
doi_str_mv | 10.1002/jpln.201900139 |
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The coffee variety Catuai required 32% more water per g plant biomass than the variety Yellow Caturra, but had a 49% lower leaf area, 34% less shoot and 46% less root biomass. Maize and mucilage amendments did not affect leaf area, shoot and root yield, or the N concentration in shoot and root dry matter. The amendments always reduced the water use efficiency values, but this reduction was only significant in the maize+mucilage‐14 (= 14 g mucilage pot−1) treatment. Soil pH significantly increased from 4.30 in the control to 4.63 in the maize+mucilage‐14 treatment. Microbial biomass C increased by 18.5 µg g−1 soil, microbial biomass N by 3.1 µg g−1 soil, and ergosterol by 0.21 µg g−1 soil per g mucilage added pot−1. The presence of mucilage significantly reduced the microbial biomass‐C/N ratio from a mean of 13.4 in the control and maize treatments to 9.3, without addition rate and coffee variety effects. The application of non‐composted mucilage is recommended in areas where drought leads to economic losses and in coffee plantations on low fertility soils like Oxisols, where Al toxicity is a major constraint.</description><identifier>ISSN: 1436-8730</identifier><identifier>EISSN: 1522-2624</identifier><identifier>DOI: 10.1002/jpln.201900139</identifier><language>eng</language><publisher>Weinheim: Wiley Subscription Services, Inc</publisher><subject>Biomass ; Carbon/nitrogen ratio ; Coffea arabica ; Coffee ; Corn ; Drought ; Dry matter ; Economic impact ; Ergosterol ; Fermented food ; Greenhouse effect ; Greenhouses ; Leaf area ; Leaves ; microbial biomass ; Microorganisms ; Mucilage ; Plant biomass ; Plants (botany) ; Seedlings ; Soil chemistry ; Soil fertility ; Soil microorganisms ; Soil pH ; Soil treatment ; Soils ; Toxicity ; Water use ; Water use efficiency</subject><ispartof>Journal of plant nutrition and soil science, 2019-10, Vol.182 (5), p.782-790</ispartof><rights>2019 WILEY‐VCH Verlag GmbH & Co. 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The coffee variety Catuai required 32% more water per g plant biomass than the variety Yellow Caturra, but had a 49% lower leaf area, 34% less shoot and 46% less root biomass. Maize and mucilage amendments did not affect leaf area, shoot and root yield, or the N concentration in shoot and root dry matter. The amendments always reduced the water use efficiency values, but this reduction was only significant in the maize+mucilage‐14 (= 14 g mucilage pot−1) treatment. Soil pH significantly increased from 4.30 in the control to 4.63 in the maize+mucilage‐14 treatment. Microbial biomass C increased by 18.5 µg g−1 soil, microbial biomass N by 3.1 µg g−1 soil, and ergosterol by 0.21 µg g−1 soil per g mucilage added pot−1. The presence of mucilage significantly reduced the microbial biomass‐C/N ratio from a mean of 13.4 in the control and maize treatments to 9.3, without addition rate and coffee variety effects. The application of non‐composted mucilage is recommended in areas where drought leads to economic losses and in coffee plantations on low fertility soils like Oxisols, where Al toxicity is a major constraint.</description><subject>Biomass</subject><subject>Carbon/nitrogen ratio</subject><subject>Coffea arabica</subject><subject>Coffee</subject><subject>Corn</subject><subject>Drought</subject><subject>Dry matter</subject><subject>Economic impact</subject><subject>Ergosterol</subject><subject>Fermented food</subject><subject>Greenhouse effect</subject><subject>Greenhouses</subject><subject>Leaf area</subject><subject>Leaves</subject><subject>microbial biomass</subject><subject>Microorganisms</subject><subject>Mucilage</subject><subject>Plant biomass</subject><subject>Plants (botany)</subject><subject>Seedlings</subject><subject>Soil chemistry</subject><subject>Soil fertility</subject><subject>Soil microorganisms</subject><subject>Soil pH</subject><subject>Soil treatment</subject><subject>Soils</subject><subject>Toxicity</subject><subject>Water use</subject><subject>Water use efficiency</subject><issn>1436-8730</issn><issn>1522-2624</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2019</creationdate><recordtype>article</recordtype><recordid>eNqFkE1LxDAQhoMouK5ePQc8d51M-pWjLOoqRT3oOWSTtGRpm5pskf33dqno0dMMzPvMDA8h1wxWDABvd0PbrxCYAGBcnJAFyxATzDE9nfqU50lZcDgnFzHuACBlAhdks_Z1bS3tRu1a1VjqukHpPfU9Pfixb6ie59Fa07q-iVT1hkbvWto5HbwPjepd7OIlOatVG-3VT12Sj4f79_UmqV4fn9Z3VaI5K0SiVWZgy1NhWG65hsKUArcGSlOkZYq63qJSTIPVWZkxVadCAypmIOPWIHC-JDfz3iH4z9HGvdz5MfTTSYkoBC8ywHxKrebU9GKMwdZyCK5T4SAZyKMtebQlf21NgJiBL9fawz9p-fxWvfyx37kwbps</recordid><startdate>201910</startdate><enddate>201910</enddate><creator>Castaño, Martha Isabel León</creator><creator>Jannoura, Ramia</creator><creator>Joergensen, Rainer Georg</creator><general>Wiley Subscription Services, Inc</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>7T7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>P64</scope><scope>SOI</scope></search><sort><creationdate>201910</creationdate><title>Coffee mucilage impact on young coffee seedlings and soil microorganisms</title><author>Castaño, Martha Isabel León ; Jannoura, Ramia ; Joergensen, Rainer Georg</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3179-ca5d0b349d16e3c07d892bd08d74842cfb2aa1c0ec5851af49c02a1d053ed2033</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2019</creationdate><topic>Biomass</topic><topic>Carbon/nitrogen ratio</topic><topic>Coffea arabica</topic><topic>Coffee</topic><topic>Corn</topic><topic>Drought</topic><topic>Dry matter</topic><topic>Economic impact</topic><topic>Ergosterol</topic><topic>Fermented food</topic><topic>Greenhouse effect</topic><topic>Greenhouses</topic><topic>Leaf area</topic><topic>Leaves</topic><topic>microbial biomass</topic><topic>Microorganisms</topic><topic>Mucilage</topic><topic>Plant biomass</topic><topic>Plants (botany)</topic><topic>Seedlings</topic><topic>Soil chemistry</topic><topic>Soil fertility</topic><topic>Soil microorganisms</topic><topic>Soil pH</topic><topic>Soil treatment</topic><topic>Soils</topic><topic>Toxicity</topic><topic>Water use</topic><topic>Water use efficiency</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Castaño, Martha Isabel León</creatorcontrib><creatorcontrib>Jannoura, Ramia</creatorcontrib><creatorcontrib>Joergensen, Rainer Georg</creatorcontrib><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Journal of plant nutrition and soil science</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Castaño, Martha Isabel León</au><au>Jannoura, Ramia</au><au>Joergensen, Rainer Georg</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Coffee mucilage impact on young coffee seedlings and soil microorganisms</atitle><jtitle>Journal of plant nutrition and soil science</jtitle><date>2019-10</date><risdate>2019</risdate><volume>182</volume><issue>5</issue><spage>782</spage><epage>790</epage><pages>782-790</pages><issn>1436-8730</issn><eissn>1522-2624</eissn><abstract>A greenhouse pot experiment was carried out to assess the effects of fermented coffee mucilage applied as mulch together with maize leaves on the growth of young coffee plants of two different varieties and on soil microbial biomass indices. The coffee variety Catuai required 32% more water per g plant biomass than the variety Yellow Caturra, but had a 49% lower leaf area, 34% less shoot and 46% less root biomass. Maize and mucilage amendments did not affect leaf area, shoot and root yield, or the N concentration in shoot and root dry matter. The amendments always reduced the water use efficiency values, but this reduction was only significant in the maize+mucilage‐14 (= 14 g mucilage pot−1) treatment. Soil pH significantly increased from 4.30 in the control to 4.63 in the maize+mucilage‐14 treatment. Microbial biomass C increased by 18.5 µg g−1 soil, microbial biomass N by 3.1 µg g−1 soil, and ergosterol by 0.21 µg g−1 soil per g mucilage added pot−1. The presence of mucilage significantly reduced the microbial biomass‐C/N ratio from a mean of 13.4 in the control and maize treatments to 9.3, without addition rate and coffee variety effects. The application of non‐composted mucilage is recommended in areas where drought leads to economic losses and in coffee plantations on low fertility soils like Oxisols, where Al toxicity is a major constraint.</abstract><cop>Weinheim</cop><pub>Wiley Subscription Services, Inc</pub><doi>10.1002/jpln.201900139</doi><tpages>9</tpages></addata></record> |
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subjects | Biomass Carbon/nitrogen ratio Coffea arabica Coffee Corn Drought Dry matter Economic impact Ergosterol Fermented food Greenhouse effect Greenhouses Leaf area Leaves microbial biomass Microorganisms Mucilage Plant biomass Plants (botany) Seedlings Soil chemistry Soil fertility Soil microorganisms Soil pH Soil treatment Soils Toxicity Water use Water use efficiency |
title | Coffee mucilage impact on young coffee seedlings and soil microorganisms |
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